Ian Tchagra Little

Understanding and Mitigating the Impacts of Land-Use Management Strategies on Grassland Biodiversity

Ian Little holding a Black-winged Lapwing chick on the communally grazed lands.

Town/RegionCountryCategoriesDate
Dullstroom, MpumalangaSouth AfricaAfrica, Birds, Habitat18 Dec 2007

The grassland biome is the second largest in South Africa, but one of the three least protected: only 2.2% of its total area is formally conserved. In South Africa, 100 plant, 12 bird, six mammal and two butterfly species are grassland endemics. Grasslands also contain 10 of the 14 globally Threatened endemic bird species in South Africa.

The Moist Highland Grassland (the focus of this study) occur at 1400-1800 m a.s.l. and are among the most threatened biotopes in South Africa, with much having been irreversibly transformed: only 1.5% of what remains is formally conserved despite its high level of endemism and many threatened taxa. We propose to study bird diversity and reproductive success as responses to differing burning and grazing practices within the MHG with the aim of assessing which agricultural practices that utilise the natural resources of grasslands can be considered ‘conservation friendly’. Reproductive performance is deemed a better biological signal of conservation importance than simple measures of abundance and diversity.

Despite being adapted to frequent natural disturbances (fire), South African grasslands are being increasingly degraded through the cumulative influences of overgrazing, excessive burning, plantation forestry and invasion by alien plants. Most lack the ability to recover after severe disturbance, and 60% of South Africa's grasslands are already transformed by activities other than pastoralism, such as afforestation and urbanisation.

Natural fires in highveld grasslands may be as infrequent as every four years or more, and empirical studies support concern over the impacts of unnaturally frequent fires and heavy grazing. Heavy grazing (especially by sheep) and annual burning are the most common agricultural management regimes and these have very high negative impacts on biodiversity.

This study aims to identify which forms of pastoralism are compatible with biodiversity conservation: its outputs will be directly applicable to the conservation of indigenous, Threatened and endemic species. Although birds are used as the model study taxon group, all taxonomic groups are predicted to benefit from identification of, and subsequent application of, conservation-friendly management. Currently, both conservation managers and agricultural extension officers lack the biological information needed to advise on or effect sound management practices.

For more information contact ian.little@uct.ac.za

Project Update: January 2008

Cape Longclaw chicks begging for food during routin nest monitoring and chick weighing.

Frustrating early season nest searching finally yielded the first nest of the highland grassland bird breeding season on the 30th of October. Due to the high altitude (>2000m) and unpredictable conditions birds breed later and for a shorter period in this system than in other comparable systems.

This nest (African Pipit, Anthus cinnamomeus) marked the beginning of a productive breeding season with breeding attempts fluctuating in temporal peaks in. Sampling of vegetation structure along with insect abundance revealed high productivity resulting in productive reproductive output by insectivorous birds through November and December. January however revealed a shift from insectivorous to granivorous bird breeding, most likely as a result of grasses setting seed in late December.

The most predominant grassland breeding birds consisted of African Pipit Anthus cinnamomeus, Yellow-breasted Pipit Anthus chloris, African Stonechat Saxicola torquata, Cape Longclaw Macronyx capensis, Wing-snapping Cisticola Cisticola ayresii and Long-tailed Widowbird Euplectes progne.

Project Update: June 2008

Chicks in nest.

"The Moist Highland Grasslands (MGH), now experiencing sub-zero degree temperatures with very little rain, are in a state of close to zero productivity. Grasses, forbs as well as insect life forms are all but dormant. This results in the altitudinal migration of small passerines to warmer more productive systems.

In this low productivity period I am working on the data that were collected in the previous season. These data include over 240 nests that were located and monitored till either completion or failure, in order to assess comparative reproductive success. The chicks in these nests were weighed every second day to obtain growth weight information. Insects were sampled throughout the breeding season with > 35 000 insect sweeps completed through the period. Vegetation was also sampled as vegetation structure is critical for nest construction and concealment. Over 60 000 vegetation sample points were measured in this season.

From these considerable data and those collected in the coming seasons I hope to extract patterns and processes explaining optimal land-use strategies for conservation in the MHG."

Final Report

Read about the activities undertaken and findings of this project in the final report below.

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Final Report.doc694.5 KB
2nd RSG Grant Awarded

Read about the latest development and plans for this project http://www.ruffordsmallgrants.org/rsg/projects/ian_tchagra_little_0


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